Anyone paying attention to the Atlantic States Marine
Fisheries Commission’s Annual Meeting last week knows that it was not a good
week for conservation.
The
annual catch limit for Atlantic menhaden was reduced by a bit, but by nowhere
near as much as a recent stock assessment update suggested was needed. A day later, multiple
members of the Atlantic Striped Bass Management Board admitted that the striped
bass stock was headed for serious trouble in the next decade, but took
no meaningful action that might help, in any way, to avert that pending crisis. And although I’m not too familiar with the
red drum fishery in the South Atlantic, friends who are have been critical of measures
adopted to manage that fishery, too.
I don’t agree with the actions taken with respect to the
menhaden limit, nor do I agree with the inaction with respect to striped
bass. At the same time, I understand the
arguments underlying the management boards’ decisions in those fisheries, and
believe that at least the majority of the Atlantic Menhaden and Atlantic
Striped Bass management board were acting in good faith when they cast their
votes.
I cannot say the same for some of the organizations that
commented on the menhaden and striped bass proposals, comments that saw such
organizations speaking out of both sides of their mouths, perhaps trying to
convince the public of their good intentions, but making it clear, to anyone
that cared to read the comments that they submitted, that they were engaging in
hypocrisy of the first order.
“Fishing Atlantic menhaden below their [ecosystem reference
point fishing mortality] target is necessary to support striped bass
rebuilding. The [ecosystem reference
point] framework explicitly links menhaden harvest levels to striped bass
population outcomes…By reducing fishing mortality below the [ecosystem
reference point fishing mortality] target, additional forage is left in the
system, lowering the probability of prey limitation on striped bass growth,
survival, and recruitment. This precautionary
strategy also accounts for uncertainty in stock assessments, predator-prey
interactions, and environmental variables, thereby increasing the likelihood
that striped bass can rebuild to their biomass target, within the mandated time
frame under the ASMFC’s rebuilding requirements.”
The letter was signed by the CCA, along with eleven other
organizations, including BoatUS, the Marine Retailers Association of the
Americas, and the Theodore Roosevelt Conservation Partnership, and anyone
reading it could easily believe that all of the signatories were honestly concerned
about striped bass conservation, at least until they reached this paragraph, which
contains some questionable, and probably intentionally deceiving, claims and
might raise some readers’ doubts:
“The ASMFC has two primary levers to support striped bass
rebuilding: controlling striped bass fishing mortality and menhaden fishing
mortality. The Atlantic Striped Bass
Board has already demonstrated leadership by implementing multiple years of
regulatory changes that reduced fishing pressure to a 30 year low, with striped
bass fishing mortality now well below the target and threshold. This means that striped bass fishing mortality
is no longer the limiting factor for rebuilding…If the ASMFC also wants to
rebuild the striped bass stock, then it needs to manage equally among both
species…”
After the Atlantic Menhaden Management Board failed to the
2026 annual catch limit to the level proposed in the letter—a
level that reflected a 50% probability of not overfishing, according to the
latest stock assessment update—the
Coastal Conservation Association put out a press release blasting the
management board’s actions, announcing that
“Fisheries Managers Fail to Protect Menhaden, Striped Bass,”
and that
“This week, the Atlantic States Marine Fisheries Commission
voted to allow an Atlantic menhaden catch that will not leave enough menhaden
in the water for striped bass. Catch was
set at 186,000 [metric tons], when scientists said that a quota of 108,000
[metric tons] was necessary to have a 50% chance of success of rebuilding the
striped bass fishery…”
Again, the language is more than a little misleading, and
that was probably intentional. Shortly
after that release was sent out, the Coastal Conservation Association’s
Maryland chapter issued its own release, using different language to send the
same inaccurate message, beginning:
“Revised models indicate the need to cut commercial [menhaden]
quota by more than half to rebuild striped bass populations.”
“’Rebuilding the Atlantic striped bass population has always
involved more than just regulating striped bass harvest. It’s also about ensuring that enough of their
key food sources, Atlantic menhaden, remains available in the water,’ said
Chris Macaluso, director of the Center for Fisheries for the Theodore Roosevelt
Conservation Partnership. ‘The Menhaden
Management Board’s decision to adopt only a 20 percent reduction in menhaden
harvest, despite the science and input from ASMFC’s own scientists who
highlighted the risks, makes it more challenging to achieve striped bass
rebuilding by 2029…”
As noted earlier, all of those comments overstate the connection
between striped bass rebuilding and cutting menhaden landings. Striped bass are a generalist predator that, over
the course of their lives, feed on everything from alewives to
zooplankton. The
most recent benchmark stock assessment informs us that
“Adult striped bass consume a variety of fish (e.g., Brevoortia
tyrannus [Atlantic menhaden], Anchoa mitchili [bay anchovy], Mendia
spp. [silversides]) and invertebrates (e.g., Callinectes sapidus [blue
crab], Cancer irroratus [Atlantic rock crab], Homarus americanus [American
lobster]), but the species consumed depends on predator size, time of year, and
foraging habitat…[One study] found that that small striped bass (a mean [fork
length] of 276 mm [<11 inches]) consumed more invertebrates while large
striped bass (a mean [fork length] of 882 mm [<35 inches]) relied more on
pelagic fish prey (such as bay anchovies and age-0 clupeids [members of the
herring family] in current years than they did in the 1950s…
“…In recent years, particular interest was paid to the role
of striped bass as a predator of Atlantic menhaden. To assess the role of striped bass, ASMFC
developed a version of the multispecies [virtual population analysis] with
striped bass, bluefish, and weakfish as menhaden predators. The MSVPA-X predicted that Atlantic Menhaden
comprised a moderate proportion of striped bass diet biomass (15-30%) and those
consumed consisted largely of age-0 and age-1 Atlantic menhaden. However, diet studies of large striped bass
by [other researchers] suggested a greater role of Atlantic menhaden of all
ages in striped bass diets. Atlantic
Menhaden were often dominant prey in studies of striped bass diets in the
Chesapeake Bay and the mid-Atlantic region, and were important prey in New
England waters. [references omitted]”
Thus, it’s clear that while menhaden are certainly an
important prey for striped bass, saying things like “Fishing Atlantic menhaden
below their [ecosystem reference point fishing mortality] target is necessary
to support striped bass rebuilding,” ““Revised models indicate the need to cut
commercial [menhaden] quota by more than half to rebuild striped bass
populations,” and “scientists said that a quota of 108,000 [metric tons] was
necessary to have a 50% chance of success of rebuilding the striped bass
fishery…” overstate that importance—striped bass have plenty of other forage
fish available to make up for a menhaden shortfall—and distort not only
reality, but the credibility of those making such claims.
Similarly, such comments demonstrate a deep misunderstanding
of the
Atlantic menhaden stock assessment that is based on ecosystem reference points
(another, single-species stock assessment is also conducted). In that assessment
“The [ecosystem reference point] target was defined as the
maximum [fishing mortality rate] on Atlantic menhaden that would sustain
striped bass at their biomass target when striped bass were fished at their
[target fishing mortality rate]. The ERP
threshold was defined as the maximum [fishing mortality rate] that would keep
striped bass at their biomass threshold when striped bass are fished at their
[threshold fishing mortality rate].”
However, although the menhaden management plans talk about “ecosystem”
reference points,
the only species considered in the 2019 Atlantic Menhaden Ecological
Reference Point Stock Assessment Report are Atlantic menhaden, striped
bass, bluefish, spiny dogfish, and weakfish, with Atlantic herring
“included as a key alternative prey to Atlantic menhaden for
the predators identified.”
Other important forage species for striped bass, such as bay
anchovy, silversides, and sand eels, were not considered in the assessment,
even though they would all be “key alternative prey” for the striped bass. And that’s perfectly reasonable, because the
purpose of that stock assessment was to determine a sustainable population
level for menhaden, not to determine the trajectory of the striped bass
population based on menhaden availability alone. To try to use it for the latter purpose, as
the various organizations commenting on future menhaden harvest levels did, was
a gross misuse of the menhaden assessment.
Still, based just on their comments to the Atlantic Menhaden
Management Board, one might excusably come to the conclusion that such
organizations truly cared about striped bass rebuilding. One must read their comments to the Atlantic
Striped Bass Management Board, in stark opposition to any reduction in recreational
striped bass harvest, to understand that such purported concern was little more
than a cloak camouflaging their cupidity and abject hypocrisy.
After all, it’s always easier to manage someone else’s fish.
But if you want to have real credibility as a conservation
advocate, you need to be willing to sustainably manage your own fishery, and make
whatever necessary sacrifices that may require.
Thus, lowering the menhaden harvest is an easy target for
the various fishing tackle, boating, and anglers’ rights organizations. After all, the organizations’ members don’t
fish for menhaden to take home and eat, they don’t intentionally catch and
release them, and they don’t manufacture and sell boats and equipment to a
menhaden fishery that is almost entirely commercial. The organizations have nothing to lose if
menhaden landings go down.
Thus, they can advocate for menhaden conservation with
complete impunity, and use the health of the striped bass stock as an excuse
for doing so.
But the easiest way to increase the striped bass
population isn’t lowering menhaden landings, but rather lowering landings of the
striped bass themselves. That’s
what the draft Addendum III to Amendment 7 to the Interstate Fishery
Management Plan for Atlantic Striped Bass proposed to do, by reducing
fishing mortality by 12% through a closed season in the ocean fishery and complimentary
measures in the Chesapeake Bay.
That proved to be a completely unacceptable option for the same
organizations.
After all, the striped bass fishery is the most important
recreational fishery on the East Coast.
Many recreational fishermen catch striped bass to take home and eat, and
even for those who choose to return their fish to the water, a closed season, particularly
one that did not permit catch-and-release during the closure, would be a hardship. And when anglers can’t or won’t fish, the
tackle industry sells less merchandise, and the boating industry’s sales might
be impacted, too.
So, while those industry and anglers’ rights organizations
might like to give lip service to the merits of conservation, particularly when
they won’t be affected by the relevant conservation measures, when conservation
strikes home and might cost them something, it starts looking a
lot more like a problem than a worthwhile goal.
Suddenly, taking a precautionary approach to management
suddenly seemed like a bad idea, and uncertainty in the data became an excuse
for inaction.
It seems that, while causing some level of economic distress
to the commercial menhaden fishery is merely an unfortunate but necessary side
effect on needed conservation measures, causing any level of economic distress
to the fishing tackle and boating industries, in order to conserve striped bass,
is unnecessary, completely unacceptable, and must not take place.
The organizations concluded their letter by writing,
“The current striped bass management plan is effective, with
fishing mortality well below target levels and protective measures successfully
guiding rebuilding efforts toward the 2029 goal. Draft Addendum III’s proposed 12% reduction,
driven by imprecise data and an ineffective approach to managing recreational
fisheries, lacks a clear conservation basis and risks unnecessary economic harm…We
urge ASMFC to maintain existing seasons to ensure continued progress without
imposing undue burdens on anglers.”
It’s a funny thing, but they don’t mention menhaden at all.
In fact, they claim that “the current striped bass
management plan is effective,” and “successfully guiding rebuilding efforts
toward the 2029 goal,” apparently even though menhaden management isn’t up to
their proposed standards.
That’s a lot different from, say, the Coastal Conservation
Association’s claim that “a quota of 108,000 [metric tons] was necessary
to have a 50% chance of success of rebuilding the striped bass fishery.”
So, what we end up with is a group of organizations willing
to use the health of the striped bass stock as an excuse to cut menhaden landings,
who then argue that cutting striped bass landings to improve the health of the
striped bass stock is a bad idea.
Some might call that being “transactional.”
But hypocrisy is a much better word.
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